Abstract
Ants deposit trail pheromones that guide nestmates to food sources. We tested the hypotheses that ant community members (Western carpenter ants, Camponotus modoc; black garden ants, Lasius niger; European fire ants, Myrmica rubra) (1) sense, and follow, each other’s trail pheromones, and (2) fail to recognize trail pheromones of allopatric ants (pavement ants, Tetramorium caespitum; desert harvester ants, Novomessor albisetosus; Argentine ants, Linepithema humilis). In gas chromatographic-electroantennographic detection analyses of a six-species synthetic trail pheromone blend (6-TPB), La. niger, Ca. modoc, and M. rubra sensed the trail pheromones of all community members and unexpectedly that of T. caespitum. Except for La. niger, all species did not recognize the trail pheromones of N. albisetosus and Li. humilis. In bioassays, La. niger workers followed the 6-TPB trail for longer distances than their own trail pheromone, indicating an additive effect of con- and hetero-specific pheromones on trail-following. Moreover, Ca. modoc workers followed the 6-TPB and their own trail pheromones for similar distances, indicating no adverse effects of heterospecific pheromones on trail-following. Our data show that ant community members eavesdrop on each other’s trail pheromones, and that multiple pheromones can be combined in a lure that guides multiple species of pest ants to lethal food baits.
Keywords: Lasius niger, black garden ant, Camponotus modoc, Western carpenter ant, Myrmica rubra, European fire ant, trail pheromone, eavesdropping, pheromonal communication, gas chromatographic-electroantennographic detection
1. Introduction
Ant colonies use multimodal communication signals to coordinate specific tasks such as foraging, nest defense, and cooperative brood care [1]. Trail pheromone signals are particularly important in the context of foraging [2]. When a forager has located a profitable food source and then returns to her nest, she deposits trail pheromones that guide nest mates to the same resource [2]. Additional foragers recruited to this resource may also deposit trail pheromones and thus reinforce the original trail [2,3], effectively resulting in collective decisions by nestmates as to which resource to exploit [3,4].
Pheromone trails leading to persistent food sources are generally well maintained by foragers [2] and thus are readily exploited by (heterospecific) non-nestmates [1,5] that learn about the location of profitable food sources through eavesdropping [6,7,8,9]. We use the term “eavesdropping” here to describe the behavior of ants gleaning trail pheromone information from community members but not to imply inevitably adverse effects for any community member involved. Indeed, aggressive encounters of ants with non-nest mates on shared (eavesdropped) trails [1,8,9] are kept to a minimum, in part, by using dissimilar foraging schedules. Temporal partitioning of activity schedules has been reported for workers of Ca. pennsylvanicus and Formica subsericea that forage on the same aphid-infested trees but at different times of the day [10], and for workers of Ca. beebei that follow trails of Az. charifex when Azteca ants are resting [1,6,8,9]. We anticipate that mutual recognition of pheromone trails is more likely for co-evolved ant species than for native and invasive species. However, two exceptions are conceivable. First, the invasion event took place a long time ago and, over time, the invading species has become a well-established and integrated community member. Second, the invading species is closely related to native species and thus produces a similar trail pheromone.
Ant communities in the Lower Mainland of British Columbia (BC), Canada are complex and comprise both native and invasive species. For the purpose of this study, we have selected three species that co-exist in the same community: (1) the Western carpenter ant, Camponotus modoc (Formicinae), which is considered native to the Pacific Northwest and has been recorded in BC as early as 1919 [11]; (2) the black garden ant, Lasius niger (Formicinae), which is native to Europe, and possibly to North America, having been recorded in the New World as early as 1979 [11,12,13]; and (3) the European fire ant, Myrmica rubra (Myrmicinae), which is native to Europe but has invaded the Pacific Northwest and other parts of North America, likely in the first decade of the 20th century [14,15]. While Ca. modoc and La. niger have co-existed for at least 39 years [13], M. rubra as a more recent adventive is known to have occurred in ant communities of BC’s Lower Mainland for nearly 20 years [15] and has already become a well-established and integrated community member. During 20 years of co-existence, all three species might have “learned” to sense each other’s trail pheromones.
We prepared the trail pheromone components currently known for these three species (Ca. modoc: (2S,4R,5S)-2,4-dimethyl-5-hexanolide (henceforth “hexanolide”) [16]; La. niger: 3,4-dihydro-8-hydroxy-3,5,7-trimethylisocoumarin (henceforth “isocoumarin”) [17]; M. rubra: 3-ethyl-2,5-dimethylpyrazine [18]) in a synthetic blend (Table 1). This blend also contained 3-ethyl-2,6-dimethyl pyrazine (a non-natural isomer in the commercial source of the M. rubra trail pheromone). To determine whether Ca. modoc, La. niger, and M. rubra sense the trail pheromones not only of community members but also of allopatric ant species, we expanded the synthetic blend to include the trail pheromone of the pavement ant, Tetramorium caespitum (2,5-dimethylpyrazine), the desert harvester ant, Novomessor albisetosus (4-methyl-3-heptanone), and the Argentine ant, Linepithema humilis ((Z)-9-hexadecenal) [19,20,21].
Table 1.
Study Species | Name of Pheromone (Amount Tested; Ant Equivalents (AEs)) | Pheromone Structures (Synthetic Sources a–e) |
---|---|---|
Ca. modoc | (2S,4R,5S)-2,4-Dimethyl-5-hexanolide (7.5 ng; 2 AEs) (“hexanolide”) [16] |
(a) |
La. niger | 3,4-Dihydro-8-hydroxy-3-7-trimethylisocoumarin (0.5 ng; 1 AE) (“isocoumarin”) [17] | (a) |
M. rubra | 3-Ethyl-2,5-dimethylpyrazine (5 ng; 1 AE) [18] | (b) |
T. caespitum | 2,5-Dimethylpyrazine (1 ng; 1 AE) [19] | (c) |
N. cockerelli | 4-Methyl-3-heptanone (10 ng;1 AE) [20] | (d) |
Li. humilis | (Z)-9-Hexadecenal (10 ng; 1 AE) [21] | CH3-(CH2)4-CH=CH-(CH2)7-CHO (e) |
(a) Synthesized as described by Renyard et al. [16]; (b) Acros Organics, New Jersey, USA (contains 3-ethyl-2,5-dimethylpyrazine at 50%); (c) Aldrich Chem Co. Milwaukee, WI, USA; (d) oxidized from 4-methyl-3-heptanol (Sigma-Aldrich, St. Louis, MO, USA); (e) oxidized from (Z)-9-hexadecenol (Sigma-Aldrich).
Here, we tested the hypotheses that sympatric Ca. modoc, La. niger, and M. rubra (1) sense, and behaviorally respond to, each other’s trail pheromones, and (2) fail to recognize the trail pheromones of allopatric ant species (T. caespitum, N. albisetosus, Li. humilis).
2. Materials and Methods
2.1. Experimental Insects
2.1.1. Lasius Niger
Between 13 and 31 August (2018), 5–10 ants were collected in various containers from each of 20 sites throughout Vancouver and Burnaby, BC. Ants were bioassayed within 24 h of collection, and then cold-euthanized for taxonomic confirmation using multiple keys [13,22,23,24].
2.1.2. Camponotus Modoc
Collection and maintenance of Ca. modoc nests have recently been described in detail [16]. Briefly, infested log sections were kept in large plastic bins (64 cm × 79 cm × 117 cm) in an outdoor undercover area exposed to natural light and temperature cycles throughout the year. Each plastic bin housing a nest was connected via clear PVC tubing (2.54 cm I.D., Nalgene™ 180; Sigma-Aldrich, St. Louis, MO, USA) to a glass aquarium (51 × 28 × 30 cm), which served as the ants’ foraging area provisioned with blow flies, live mealworms, honey, apples, canned chicken, and 20% sugar water, all ad libitum.
2.1.3. Myrmica Rubra
In the spring and summer of 2017 and 2018, 20 nests of M. rubra were dug out of the ground at Inter River Park (North Vancouver, BC, Canada), the Regional Allotment Garden (Burnaby, BC, Canada), and the VanDusen Botanical Garden (Vancouver, BC, Canada). Nests were kept indoors in the Science Research Annex of Simon Fraser University (49°16′33″ N, 122°54′55″ W) at 25 °C and a photoperiod of 12 h L to 12 h D. Nests were housed in small Tupperware dishes (15 × 15 × 9 cm) (Rubbermaid®, Newell Brands, Atlanta, GA, USA & Royal Sponge Manufacturing Ltd., Toronto, ON, Canada), which were fitted with sterilized potting soil as nesting material and placed inside a small or large tote (41 × 29 × 24 cm; 58 × 43 × 31 cm) that served as the ants’ foraging area. Twice a week, the nests were sprayed with water and provisioned with food (fruits, nuts, mealworms, and processed meat). Test tube water reservoirs were replaced when low.
2.2. Gas Chromatographic-Electroantennographic Detection (GC-EAD) Analyses of Synthetic Ant Trail Pheromones
For GC-EAD analyses and behavioral bioassays, a synthetic blend of six ant trail pheromones (see above), henceforth six-trail pheromone blend (6-TPB; Table 1), was prepared. The blend was analyzed by gas chromatographic-electroantennographic detection (GC-EAD), with procedures and equipment previously described in detail [25,26]. Briefly, the GC-EAD setup employed a Hewlett-Packard 5890 gas chromatograph (GC) fitted with a DB-5 GC column (30 m × 0.32 mm I.D.; J&W Scientific, Folsom, CA, USA). Helium served as the carrier gas (35 cm·s−1) with the following temperature program: 50 °C for 1 min, 20 °C·min−1 to 280 °C. The injector port and flame ionization detector (FID) were set to 260 °C and 280 °C, respectively. For GC-EAD recordings (three antennae each for Ca. modoc, La. niger, and M. rubra), an antenna was carefully dislodged from a worker ant and suspended between two glass capillary electrodes (1.0 × 0.58 × 100 mm; A-M Systems, Carlsborg, WA, USA) prepared to accommodate the antenna and filled with a saline solution [27].
2.3. General Design of Trail-Following Bioassays
All bioassays were run within a metal scaffold (123 × 57 × 36 cm) encased in black fabric to eliminate external visual stimuli, lit from above with two fluorescent lights (48″ 32 W F32T8, one plant and aquarium bulb, and one daylight bulb, Phillips, Amsterdam, The Netherlands), and fitted with a video camera (Sony HDR CX210, Sony, Tokyo, Japan or Canon FS100 A, Canon, Tokyo, Japan) mounted above the bioassay arena (Figure 1). The edges of the bioassay arenas (see below) were coated with a mixture of petroleum jelly and mineral oil to prevent the escape of bioassay ants.
The specific experimental design to test trail-following responses accounted for body size differentials of large ants (Ca. modoc) and small ants (La. niger and M. rubra). The design for testing Ca. modoc was previously described [16] and is outlined here. Camponotus modoc was tested in a large plexiglass arena (64 × 44 × 10 cm) fitted with a filter paper (18.5 cm diam; Sigma-Aldrich, St. Louis, MO, USA), with its circular circumference marked with pencil in 1 cm intervals (58 marks total) and treated with one of three test stimuli (see below) at 1–2 ant equivalents (AE)/58 µL. Each bioassay ant (n = 60) entered the arena by exiting a 15 mL Falcon™ “holding” tube (Thermo Fisher Scientific, Waltham, MA, USA) through a hole cut in its tapered tip.
Lasius niger and M. rubra were tested in a Pyrex petri dish (15 cm diam) fitted with a small circular filter paper (9.0 cm diam), with its circumference marked with pencil in 1 cm intervals (25 total) and treated with one of three test stimuli (see below) at 1–2 AEs/25 µL. Each worker ant of La. niger (n = 60) and M. rubra (n = 60) entered the Petri dish by exiting a 1.5 mL Axygen™ MaxyClear Snaplock “holding” microtube (Thermo Fisher Scientific, Waltham, MA, USA) through a hole cut in its tapered tip. Bioassays of large and small ants were initiated by removing the cotton plug from the exit hole of a holding tube and were terminated after 5 min (Ca. modoc) and 10 min (La. niger and M. rubra). Filter papers were prepared for bioassays by applying a continuous trail of test stimulus [(i) synthetic 6-TPB; (ii) synthetic trail pheromone of the bioassay ant; or (iii) a solvent control; Table 1].
The number of 1 cm intervals an ant had followed during a bioassay served as the response criterion and was analyzed by viewing the video footage. Ants not leaving their holding tube after 10 min were considered non-responders and excluded from analyses. Between bioassays, all preparative surfaces and bioassay arenas were cleaned with 70% EtOH and hexane, and the experiment room was aired out for 5 to 10 min by opening an exterior door. A new ant was tested for each treatment. All La. niger and M. rubra ants were collected from different laboratory or field colonies. Worker ants of Ca. modoc were collected from six colonies maintained in an outdoor enclosure.
2.4. Statistics
R (Version 3.5.0; multicomp, plotrix, & plyr packages) was used to analyze the data and produce graphics [28,29,30]. A generalized linear model (GLM; quasi-Poisson distribution) was used to analyze the distances ants travelled following trails in response to the various types of trails presented. An analysis of variance (ANOVA) and Tukey’s honest significant difference (HSD) test were used to determine significant differences in mean distance travelled in response to trail type.
3. Results
3.1. Gas Chromatographic-Electroantennographic Detection (GC-EAD) Analyses of Synthetic Ant Trail Pheromones
In GC-EAD analyses, La. niger antennae responded to (in the order of elution) synthetic 2,5-dimethylpyrazine, 4-methyl-3-heptanone, 3-ethyl-2,5-dimethylpyrazine, 3-ethyl-2,6-dimethyl pyrazine, hexanolide, isocoumarin (its own trail pheromone), and (Z)-9-hexadecenal (Figure 2; Table 2). Antennae of Ca. modoc responded to 2,5-dimethylpyrazine, 3-ethyl-2,5-dimethylpyrazine, 3-ethyl-2,6-dimethyl pyrazine, hexanolide (its own trail pheromone), and isocoumarin (Figure 2; Table 2). Antennae of M. rubra responded to 2,5-dimethylpyrazine, 3-ethyl-2,5-dimethylpyrazine (its own trail pheromone), 3-ethyl-2,6-dimethyl pyrazine, hexanolide, and isocoumarin (Figure 2; Table 2).
Table 2.
Distribution | Species | Trail Pheromone | Produced by/Antennal Response | ||
---|---|---|---|---|---|
La. niger | Ca. modoc | M. rubra | |||
Sympatric | La. niger | Isocoumarin * | yes/yes | yes/yes | no/yes |
Ca. modoc | Hexanolide ** | no/yes | yes/yes | no/yes | |
M. rubra | 3-Ethyl-2,5-dimethylpyrazine | no/yes | no/yes | yes/yes | |
Allopatric | T. caespitum | 2,5-Dimethylpyrazine | no/yes | no/yes | no/yes |
N. albisetosus | 4-Methyl-3-heptanone | no/yes | no/no | no/no | |
Li. humilis | (Z)-9-Hexadecenal | no/yes | no/no | no/no |
* 3,4-Dihydro-8-hydroxy-3,5,7-trimethylisocoumarin; ** 2,4-Dimethyl-5-hexanolide.
3.2. Trail-Following Bioassays
There were significant differences in the distances (mean ± SE) that worker ants of La. niger travelled following trails of the 6-TPB (495.5 ± 57.5 cm), the isocoumarin (199.3 ± 43.1 cm), and the solvent control (32.2 ± 14.0 cm) (ANOVA, F = 34.028, degrees of freedom (df) = 2, residual df = 57, p < 0.001; Figure 3). Based on Tukey’s HSD tests, all distances differed from one another (pairwise comparisons: Isocoumarin vs. solvent control: p = 0.001; 6-TPB vs. solvent control: p < 0.001; 6-TPB vs. isocoumarin: p < 0.001).
There were also significant differences in the distances that worker ants of Ca. modoc travelled following trails of the 6-TPB (213.1 ± 48.7 cm), the hexanolide (206.0 ± 32.7 cm), and the solvent control (69.1 ± 12.6 cm) (ANOVA, F = 7.5583, df = 2, residual df = 57, p < 0.01; Figure 4). Based on Tukey’s HSD tests, distances were different between the 6-TPB and the solvent control (p < 0.01), and between the hexanolide and the solvent control (p < 0.01), but were statistically the same between the 6-TPB and the hexanolide (p = 0.99).
There were no significant differences in the distances that worker ants of M. rubra travelled following trails of the 6-TPB (22.9 ± 8.7 cm), the 3-ethyl-2,5-dimethylpyrazine (41.2 ± 8.3 cm), and the solvent control (32.9 ± 8.1 cm) (ANOVA, F = 1.1555, df = 2, residual df = 57, p = 0.3222; Figure 5).
4. Discussion
As predicted, La. niger, Ca. modoc, and M. rubra did sense (antennally respond to) the trail pheromone of all community members (La. niger, Ca. modoc, M. rubra; Figure 2) and, except for La. niger, did not recognize the trail pheromones of two allopatric ant species (N. cockerelli and Li. humilis; Table 2). That all three ant species sensed the trail pheromone of allopatric T. caespitum could be due its molecular structure (2,5-dimethylpyrazine) resembling that of the M. rubra trail pheromone (3-ethyl-2,5-dimethylpyrazine). In light of our behavioral data that the 6-TPB (which contains trail pheromones of con- and hetero-specifics) readily induced trail-following behavior of Ca. modoc and La. niger, it seems that these ants either simply ignore (Ca. modoc), or indeed eavesdrop on (La. niger), each other’s trail pheromone communication. In general, eavesdropping ants can face aggression, increased competition, or even displacement [1,6,8,9,10], but in the ant community we studied here, eavesdropping may accrue more benefits than harm, or at least, no harm. This inference is based on our bioassay data showing that (i) La. niger workers followed trails of the 6-TPB for a longer distance than they followed their own trail pheromone (isocoumarin), and (ii) Ca. modoc workers followed trails of the 6-TPB and their own pheromone (hexanolide) for similar distances.
Unexpectedly, workers of M. rubra followed trails of the 6-TPB and their own trail pheromone (3-ethyl-2,5-dimethylpyrazine) only as much as a solvent control trail, demonstrating no effect of the trail pheromone in this type of bioassay. There are at least two explanations why M. rubra did not follow a trail of synthetic 3-ethyl-2,5-dimethylpyrazine. Prior studies that demonstrated distinct trail following by M. rubra, either in “no-choice bioassays” comparable to our experimental design [18] or in “binary-choice arena bioassays” [31], tested the responses of multiple workers (the entire nest), whereas we tested the responses of individual ants. Given the small foraging range and high nest density of M. rubra in North America [31,32], it is conceivable that nest mates do not forage on their own but engage in group foraging, as shown in many Myrmica species [33]. Group foraging entails cooperative interactions, where, for example, a successful forager recruits nestmates and physically guides them to the food source [33]. Group foraging may improve the overall foraging effort of a nest and facilitate transport of food particles that are too heavy for single ants to carry [34]. Alternatively, the trail pheromone blend of M. rubra comprises not only 3-ethyl-2,5-dimethylpyrazine but additional pheromone components, which, thus far, have eluded identification.
The evidence presented here that some ant community members eavesdrop on and exploit each other’s trail pheromone has major implications for ant control. Food baits laced with lethal agents show promise as an ant control tactic because many ants share food through trophallaxis and thus may spread the poison together with the food throughout their entire nest. The effect of lethal food baits can be enhanced by adding attractants. For example, the admixture of trail pheromone to food baits increased bait consumption by the invasive Argentine ant, L. humile [35]. In M. rubra, a path of synthetic trail pheromone leading from a nest to a food bait is more effective in recruiting foragers than applying the trail pheromone around a food bait [31].
Commercial development of trail pheromones for ant control is contingent upon economic feasibility. With so many important ant species in need of control, and with each species producing its own trail pheromone, manufacturing species-specific (single target) trail pheromone lures (ropes, strings) does not seem economically viable. However, if trail pheromones of multiple ant species were to be combined in a single lure (multiple targets), with potential synergism and no antagonism between components, as shown in our study, then an ant control tactic that couples a lethal food bait with a trail pheromone lure seems commercially feasible. As an added advantage, the ant species targeted for control would not even need to be identified by a pest control professional or the lay person buying the control technology in a retail store.
Future studies should aim to strengthen the proof of concept presented in our study. Trail pheromones of major ant pests such as the red imported fire ant, Solenopsis invicta, should be added to the multiple-species trail pheromone lure and tested for the response of S. invicta and other species. Moreover, research needs to be initiated on dispensers capable of sustained release of trail pheromones in field experiments and, eventually, operational applications.
5. Conclusions
All three select members of ant communities in the Lower Mainland of BC (La. niger, Ca. modoc, M. rubra) sensed each other’s trail pheromone and, except for La. niger, did not recognize the trail pheromones of two allopatric ant species (N. cockerelli and Li. humilis). Workers of La. niger followed a synthetic trail pheromone blend (containing the trail pheromone of all three community members and those of three allopatric ant species) for a longer distance than they followed their own trail pheromone, and Ca. modoc workers followed this blend and their own trail pheromone for similar distances. Apparently, these ants either ignore (Ca. modoc), or indeed eavesdrop on (La. niger), each other’s trail pheromone. Eavesdropping ants may accrue benefits by learning about the location of profitable food sources. If synthetic trail pheromones of multiple pest ant species were to be combined in a single (rope-type) lure, with potential synergism and no antagonism between components (as shown in our study), an ant control tactic that presents a lethal food bait together with a trail pheromone lure seems commercially viable.
Acknowledgments
We thank Robert Higgins and Laurel Hansen for identification of ant species, Michael Gudmundson for assisting with field collections of Ca. modoc, Grady Ott for providing nest bins, Jan Lee, Ashley Munoz, Shelby Kwok, Sebastian Damin, Stephanie Fan, Kris Cu, Hanna Jackson, Jessica Chalissery, Rosemary Vayalikunnel, and Zhanata Almazbekova for assistance with colony maintenance (all species), field collections of M. rubra, and experiments.
Author Contributions
Conceptualization, J.M.C., A.R., R.G., D.H. and G.G.; methodology, J.M.C., A.R., R.G., D.H. and G.G.; validation, J.M.C., A.R., R.G., D.H. and G.G.; formal analysis, J.M.C., A.R. and R.G.; investigation, J.M.C., A.R. and R.G.; resources, J.M.C., A.R., R.G., D.H., S.K.A. and G.G.; data curation, J.M.C. and A.R.; Writing—Original draft preparation, J.M.C., R.G. and G.G.; Writing—Review and editing, J.M.C., A.R., R.G., D.H. and G.G.; visualization, J.M.C. and S.K.A.; supervision, J.M.C., A.R., R.G., D.H. and G.G.; project administration, J.M.C., R.G. and G.G.; funding acquisition, J.M.C., D.H., A.R. and G.G.
Funding
This research was supported by a Vice President Research-Undergraduate Student Research Award from Simon Fraser University (SFU) and a Graduate Entrance Scholarship to J.M.C.; a Graduate Fellowship from SFU and a Natural Sciences and Engineering Research Council of Canada (NSERC)-CGSM to A.R.; a Graduate Fellowship from SFU and a Thelma Finlayson Graduate Fellowship to D.H., and by an NSERC-Industrial Research Chair to G.G., with Scotts Canada Ltd. as an industrial sponsor.
Conflicts of Interest
The authors declare no conflict of interest. The funders had no role in the design of the study; in the collection, analyses, or interpretation of data; in the writing of the manuscript, or in the decision to publish the results.
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